Brazilian Atlantic Islands: Fernando de Noronha and Atol das Rocas Reserves
Country
Brazil
Inscribed in
2001
Criteria
(vii)
(ix)
(x)
The conservation outlook for this site has been assessed as "significant concern" in the latest assessment cycle. Explore the Conservation Outlook Assessment for the site below. You have the option to access the summary, or the detailed assessment.
Peaks of the Southern Atlantic submarine ridge form the Fernando de Noronha Archipelago and Rocas Atoll off the coast of Brazil. They represent a large proportion of the island surface of the South Atlantic and their rich waters are extremely important for the breeding and feeding of tuna, shark, turtle and marine mammals. The islands are home to the largest concentration of tropical seabirds in the Western Atlantic. Baia de Golfinhos has an exceptional population of resident dolphin and at low tide the Rocas Atoll provides a spectacular seascape of lagoons and tidal pools teeming with fish. © UNESCO
Summary
2025 Conservation Outlook
Finalised on
11 Oct 2025
Significant concern
Current state and trend of VALUES
High Concern
Overall THREATS
Overall PROTECTION and MANAGEMENT
Full assessment
Description of values
Spectacular seascape and the highest known population of resident dolphins
Criterion
(vii)
Baía dos Golfinhos is the only know place in the world with such a high population of resident dolphins and Atoll das Rocas demonstrates a spectacular seascape at low tide when the exposed reef surrounding shallow lagoons and tidal pools forms a natural aquarium. Both sites have also exceptional submarine landscapes that have been recognised worldwide by a number of specialised diving literatures (World Heritage Committee, 2015).
A key role in the process of reproduction, dispersal and colonisation by marine organisms in the entire Tropical South Atlantic
Criterion
(ix)
Fernando de Noronha and Atol das Rocas Reserves (FNNMP/AdRBR) represents over half the insular coastal waters of the Southern Atlantic Ocean. These highly productive waters provide feeding ground for species such as tuna, billfish, cetaceans, sharks, and marine turtles as they migrate to the Eastern Atlantic coast of Africa. An oasis of marine life in relatively barren, open ocean, the islands play a key role in the process of reproduction, dispersal and colonisation by marine organisms in the entire Tropical South Atlantic (World Heritage Committee, 2015).
Marine biodiversity and endangered species of Southern Atlantic
Criterion
(x)
FNNMP/AdRBR is a key site for the protection of biodiversity and endangered species in the Southern Atlantic. Providing a large proportion of the insular habitat of the South Atlantic, the site is a repository for the maintenance of marine biodiversity at the ocean basin level, including tuna, shark and marine mammals. It is important for the conservation of endangered and threatened species of marine turtles, particularly the hawksbill and green turtles, for which the Atol das Rocas is considered the second most important breeding site of Brazil. Atol das Rocas also has the most abundant population of the brown spiny lobster and acts as a primary source for other widely distributed populations in the Central Atlantic (Gaeta et al., 2015, 2020). Baía dos Golfinhos has an exceptional population of resident spinner dolphins (World Heritage Committee, 2015).
The highly productive coastal waters around islands are used by many fish species for spawning and as a refuge for juvenile fish. The shallow waters also provide habitat for benthic organisms (such as coral, sponges and algae). 15 species of coral have been recorded of which six are endemic to Brazil. 95 species of fish have been reported in FNNMP – including two species endemic to the archipelago – while 147 species of fish have been recorded from AdRBR (IUCN, 2001).
The highly productive coastal waters around islands are used by many fish species for spawning and as a refuge for juvenile fish. The shallow waters also provide habitat for benthic organisms (such as coral, sponges and algae). 15 species of coral have been recorded of which six are endemic to Brazil. 95 species of fish have been reported in FNNMP – including two species endemic to the archipelago – while 147 species of fish have been recorded from AdRBR (IUCN, 2001).
Largest concentration of tropical seabirds in the Western Atlantic Ocean
Criterion
(x)
The site hosts the highest bird species diversity among Brazil’s oceanic islands, with 17 resident species—11 seabirds and 6 landbirds. Among these are two threatened endemic landbirds: Noronha Elaenia (Elaenia ridleyana) and Noronha vireo (Vireo gracilirostris). Additionally, four seabird species found in the area are nationally threatened: Audubon’s Shearwater (Puffinus lherminieri), Red‑billed Tropicbird (Phaethon aethereus), White‑tailed Tropicbird (Phaethon lepturus), and Red‑footed Booby (Sula sula). Around 60 migratory and vagrant bird species have also been recorded within the site. Due to this rich avifauna and the site’s critical role in bird conservation, the archipelago has been designated an Important Bird Area (Santos et al., 2024). Moreover, the site supports the largest concentration of tropical seabirds in the Western Atlantic Ocean and has been recognized as a Global Centre of Bird Endemism (World Heritage Committee, 2015). The Fernando de Noronha Archipelago and Atol das Rocas are Brazil’s most significant offshore breeding grounds in terms of both species richness and population size. Eleven seabird species breed on Fernando de Noronha, while five species breed on Atol das Rocas. Most seabird species breeding on Fernando de Noronha are widely distributed across tropical and subtropical oceans. These include the Brown Noddy (Anous stolidus), Black Noddy (Anous minutus), Sooty Tern (Onychoprion fuscatus), White Tern (Gygis alba), Brown Booby (Sula leucogaster), Masked Booby (Sula dactylatra), Red-footed Booby (Sula sula), White-tailed Tropicbird (Phaethon lepturus), Red-billed Tropicbird (Phaethon aethereus), and Magnificent Frigatebird (Fregata magnificens). Although Puffinus lherminieri (Audubon’s Shearwater) is distributed throughout tropical and subtropical regions of the western Atlantic, in Brazil it breeds regularly only on Fernando de Noronha (Mancini et al., 2016).
Only remaining sample of the Insular Atlantic Forest
Criterion
(x)
The site contains the only remaining sample of the Insular Atlantic Forest and the only oceanic mangrove in the South Atlantic region (World Heritage Committee, 2015).
The Insular Atlantic Forest – a sub-type of Atlantic Rainforest – is considered the world’s most threatened tropical forest. To date over 400 species of vascular plants have recorded in FNNMP, including three endemics. The vegetation on Atoll das Rocas is mainly herbaceous, salt resistant, and typical of sandy beaches where Cyperaceae, Gramineae and Amaryllidaceae species are predominant (IUCN, 2001).
The Insular Atlantic Forest – a sub-type of Atlantic Rainforest – is considered the world’s most threatened tropical forest. To date over 400 species of vascular plants have recorded in FNNMP, including three endemics. The vegetation on Atoll das Rocas is mainly herbaceous, salt resistant, and typical of sandy beaches where Cyperaceae, Gramineae and Amaryllidaceae species are predominant (IUCN, 2001).
Assessment information
The most serious threats to the site’s values at present are from tourism and urban growth, displacing native terrestrial species on Fernando de Noronha. Illegal fishing also threaten several of the site’s marine species and habitats. The Atol das Rocas Biological Reserve faces growing threats from global pressures such as marine heatwaves, erosion, and sea level rise, which endanger coral reefs, seabirds, and sea turtles. However, the lack of quantitative and qualitative evaluations of climate change impacts local biodiversity make a comprehensive assessment of the current threat level difficult. The risk of invasive species, especially via marine debris and ocean currents from Africa, is high and numerous invasive species are widespread across the property, impacting native flora and fauna.
Water-borne & other effluent Pollution, Garbage & Solid Waste
(Oil and plastic pollution)
Inside site
, Extent of threat not known
Outside site
Oil pollution stems from leaks and the discharge of bilge water from passenger and fishing vessels, as well as from the handling of fuels and oils at the harbor (ICMBio, 2011b). The routine delivery of fuel to the power plant on Fernando de Noronha further increases environmental risks. Prior to 2023, several incidents of waste and oil reaching the mainland, as well as the Fernando de Noronha and Atol das Rocas archipelagos, have been reported. For example, in 2019 almost 2890 km of coastline of Brazil was affected by an oil spill, and in 2021 a new event of unknown origin brought about 1.3 tons of plastics and oil to the Fernando de Noronha Archipelago (Magalhaes et al., 2020).
Most of these pollutants are neither produced nor utilized in Brazil and are believed to have been discarded in the mid-Atlantic Ocean (Zacharias et al., 2023). Both Atol das Rocas and Fernando de Noronha are also susceptible to oil spills resulting from tanker transshipments. The Port of Fernando de Noronha continues to receive cargo ships under precarious safety conditions, making oil spillage a significant localized threat. Additionally, the Brazilian Ministry of Energy has proposed oil exploration in areas near Atol das Rocas and Fernando de Noronha, which would pose a serious contamination risk in the event of a spill (State Party of Brazil, 2023). Magalhães et al. (2020) highlighted the limited governmental and local capacity to detect environmental accidents within Brazil’s Exclusive Economic Zone and to identify potential polluters. Their study underscores the vulnerability of the South Atlantic coastline and islands to the growing accidents related to the fossil fuel production chain, shipwrecks, and maritime traffic—risks that are expected to intensify with the increasing frequency of extreme climate events driven by global environmental change.
Most of these pollutants are neither produced nor utilized in Brazil and are believed to have been discarded in the mid-Atlantic Ocean (Zacharias et al., 2023). Both Atol das Rocas and Fernando de Noronha are also susceptible to oil spills resulting from tanker transshipments. The Port of Fernando de Noronha continues to receive cargo ships under precarious safety conditions, making oil spillage a significant localized threat. Additionally, the Brazilian Ministry of Energy has proposed oil exploration in areas near Atol das Rocas and Fernando de Noronha, which would pose a serious contamination risk in the event of a spill (State Party of Brazil, 2023). Magalhães et al. (2020) highlighted the limited governmental and local capacity to detect environmental accidents within Brazil’s Exclusive Economic Zone and to identify potential polluters. Their study underscores the vulnerability of the South Atlantic coastline and islands to the growing accidents related to the fossil fuel production chain, shipwrecks, and maritime traffic—risks that are expected to intensify with the increasing frequency of extreme climate events driven by global environmental change.
Invasive Non-Native/ Alien Species
(Invasive alien species)
Invasive/problematic species
Felis catus
Canis lupus
Rattus sp.
Mus musculus
Salvator merianae
Wasmannia auropunctata
Leucaena leucocephala
Lantana camara
Pterois sp.
Bubulcus ibis
Other invasive species names
Rhinella jimi, Kerodon rupestris, Tropidarus Hispidus
Inside site
, Throughout(>50%)
The clearing of native vegetation and the introduction of invasive species have significantly impacted the Fernando de Noronha site (ICMBio, 2011b; UNEP-WCMC, 2011). Although the site benefits from relatively effective management, the risk of invasive alien species being introduced remains high. This risk is largely due to the vulnerability of the atoll’s location, which is exposed to ocean currents originating from Africa and capable of transporting marine debris (Gurgel, 2023). Several research initiatives are currently underway to inform and support management plans focused on controlling the effects of invasive species, particularly on native flora, amphibians, reptiles, ground-nesting birds, and sea turtles (Instituto Brasileiro Medicina da Conservacao, 2015; Vieira, 2016; Russell et al., 2018; Abrahão et al., 2019; Soares et al., 2023; Micheletti et al., 2020; Toledo et al., 2023). Invasive species are now widespread across the island, with mammalian predators such as domestic cats (Felis silvestris catus), dogs (Canis lupus familiaris), brown and black rats (Rattus norvegicus and R. rattus), house mice (Mus musculus), cururu-toad (Rhinella jimi), tegu lizard (Salvator merianae), cattle egret (Bubulcus ibis), little fire ant (Wasmannia auropunctata), rock cavy (Kerodon rupestris), at least one lizard (Tropidarus Hispidus), and the river tamarind (Leucaena leucocephala) present throughout Fernando da Noronha island and only absent from the smaller offshore islets. Various studies demonstrate the impacts of these predators on native species (Dias et al., 2017; Mello and de Oliveira, 2016; Russell and Taylor, 2019; Gatto-Almeida, 2020). Another factor that intensifies this threat is the ecological connectivity created by a chain of seamounts, which makes the Atoll susceptible to the same oceanic system as the Fernando de Noronha Archipelago. This archipelago is a major tourist destination where the invasive lionfish (Pterois spp.) has already been recorded (Gurgel, 2023; Soares et al., 2023). According to Hidenburgo et al. (2023), lionfish are increasingly spreading along the Brazilian coast, including in both the Fernando de Noronha and Rocas Atoll archipelagos. Notably, 41% of all lionfish records in Brazil have been reported in the Fernando de Noronha Archipelago (Soares et al., 2023). Moreover, several zoonotic diseases, like salmonellosis and toxoplasmosis, have been linked to some of these invasive species (Micheletti et al., 2020). Strengthening biosecurity measures to prevent future invasions is becoming increasingly critical (IUCN Consultation, 2020). An integrated approach is essential—one that involves multiple stakeholders and combines solutions-based ecological research, real-time species inventories, updated environmental and fishery legislation, participatory monitoring, and a unified national plan to reduce the impact of lionfish (Pterois spp.) (Soares et al., 2023). However, invasive species management in Fernando de Noronha currently lacks a targeted conservation strategy and does not incorporate lethal control methods, which limits the effectiveness of efforts to mitigate biodiversity impacts, especially when considered alongside broader social and economic challenges (Russell et al., 2019).
Fishing, Harvesting & Controlling Aquatic Species
(Illegal fishing)
Inside site
, Widespread(15-50%)
This includes commercial fishing within no-take zones, as well as artisanal spear and blast fishing in coral reef communities (ICMBio, 2011b; UNEP-WCMC, 2011). Artisanal fishing for self-consumption and local income is practiced in the archipelago as an alternative to tourism. Locally, the Fernando de Noronha Reserve supports a small-scale fishery consisting of approximately ten artisanal and recreational vessels (Brunel et al., 2021).
Commercial fishing has been prohibited since 1998, following a significant decline in shark populations due to overfishing (García & Clapis, 2008). Despite this, such activities continue to have considerable negative impacts on pelagic and benthic species, as well as on sea turtles and other marine life. The majority of the catch consists of Thunnus albacares and Caranx lugubris (Domínguez et al., 2015).
Illegal fishing in Atol das Rocas is primarily carried out by oceanic fishing fleets from Northeastern Brazil. As of 2023, illegal fishing remains one of the main threats to the area, with harmful effects on fish populations and species composition.
Enforcement of fishing regulations is insufficient at both the Fernando de Noronha and Atol das Rocas Reserves. It was suggested that a new approach may be needed, involving regulation of fishing activities in the surrounding areas. In 2023, the State Party reaffirmed the need for such measures (State Party of Brazil, 2023).
Commercial fishing has been prohibited since 1998, following a significant decline in shark populations due to overfishing (García & Clapis, 2008). Despite this, such activities continue to have considerable negative impacts on pelagic and benthic species, as well as on sea turtles and other marine life. The majority of the catch consists of Thunnus albacares and Caranx lugubris (Domínguez et al., 2015).
Illegal fishing in Atol das Rocas is primarily carried out by oceanic fishing fleets from Northeastern Brazil. As of 2023, illegal fishing remains one of the main threats to the area, with harmful effects on fish populations and species composition.
Enforcement of fishing regulations is insufficient at both the Fernando de Noronha and Atol das Rocas Reserves. It was suggested that a new approach may be needed, involving regulation of fishing activities in the surrounding areas. In 2023, the State Party reaffirmed the need for such measures (State Party of Brazil, 2023).
Recreational Activities
(Tourism impacts)
Inside site
, Widespread(15-50%)
Unsustainable tourism development has led to significant degradation of both the marine environment (due to physical damage caused by anchors, novice divers, beachgoers, harbours, and sewage) and coastal and terrestrial environments (including fauna disturbance, infrastructure construction, introduction of exotic species, fauna collection as souvenirs, trampling of vegetation, and damage to scenic values) (ICMBio, 2011b; UNEP-WCMC, 2011; de Freitas, 2011). The increase in visitors poses a serious threat to biodiversity conservation. In 2022 alone, a study recorded 12,986 interactions between boats and dolphins in the region of Santo Antônio Bay and Entre Ilhas, and more than 88% of these interactions involved some type of inappropriate maneuver, such as vessels entering directly into the middle of the group and fragmenting its formation. These interferences affect the animals' movement pattern, alter their routine and compromise their rest (Cunha, 2025).
To address this issue, the Fernando de Noronha Reserve implemented strict visitation controls based on a study of carrying capacity and the development of sustainable tourism infrastructure, aimed at providing a high-quality visitor experience. However, powerful stakeholders, such as local management and those with diverse interests in the area, drive the development of the region according to their own agendas (IUCN Consultation, 2020). Cultural differences between small hotels (mainly owned by native islanders) and large hotels (owned by non-native Brazilians) further complicate cooperation between these groups, particularly within the Fernando de Noronha Reserve. Furthermore, issues such as a lack of basic sanitation, inadequate water treatment, and improper waste disposal are ongoing problems resulting from uncontrolled tourism.
The Carrying Capacity Study, conducted by a private consulting firm as part of a contract with ICMBio, recommended the prohibition of new hotel developments since 2002. Despite this, the number of hotels and accommodation facilities continues to rise—from 105 in 2005 to approximately 300 in 2021 (State Party of Brazil, 2023; IUCN Consultation, 2020). Economic pressures and barriers to the successful implementation of local tourism controls have led to an increasing number of visitors, exacerbating the region's tourism growth. For example, the number of visitors to the reserve increased from 62,500 in 2002 (the year following its inscription on the World Heritage List) to 91,000 in 2016, 106,000 in 2019, and 114,106 in 2021. This represents a 27% increase over the figure of 89,000 tourists per year recommended in the Carrying Capacity Study and the protected area management plan (Marinho, 2020). Between 2021 and 2024, Fernando de Noronha received, on average, 128 thousand visitors per year – a growth of 29% compared to the previous period. In 2024, the archipelago reached 131.5 thousand visitors, approaching the annual limit of 132 thousand tourists imposed by environmental authorities. The increase reflects the destination's growing popularity, with 11,000 more visitors than the previous year (Cunha, 2025). Additionally, Sánchez et al. (2023) notes that the growth in both tourism and permanent residents (from 2,416 islanders in 1998 to approximately 6,000 in 2021) has contributed to a rising demand for energy and increased environmental impacts.
Given these concerns, effective actions are urgently needed to address visitation and associated infrastructure developments and reduce the negative impacts on key attributes.
To address this issue, the Fernando de Noronha Reserve implemented strict visitation controls based on a study of carrying capacity and the development of sustainable tourism infrastructure, aimed at providing a high-quality visitor experience. However, powerful stakeholders, such as local management and those with diverse interests in the area, drive the development of the region according to their own agendas (IUCN Consultation, 2020). Cultural differences between small hotels (mainly owned by native islanders) and large hotels (owned by non-native Brazilians) further complicate cooperation between these groups, particularly within the Fernando de Noronha Reserve. Furthermore, issues such as a lack of basic sanitation, inadequate water treatment, and improper waste disposal are ongoing problems resulting from uncontrolled tourism.
The Carrying Capacity Study, conducted by a private consulting firm as part of a contract with ICMBio, recommended the prohibition of new hotel developments since 2002. Despite this, the number of hotels and accommodation facilities continues to rise—from 105 in 2005 to approximately 300 in 2021 (State Party of Brazil, 2023; IUCN Consultation, 2020). Economic pressures and barriers to the successful implementation of local tourism controls have led to an increasing number of visitors, exacerbating the region's tourism growth. For example, the number of visitors to the reserve increased from 62,500 in 2002 (the year following its inscription on the World Heritage List) to 91,000 in 2016, 106,000 in 2019, and 114,106 in 2021. This represents a 27% increase over the figure of 89,000 tourists per year recommended in the Carrying Capacity Study and the protected area management plan (Marinho, 2020). Between 2021 and 2024, Fernando de Noronha received, on average, 128 thousand visitors per year – a growth of 29% compared to the previous period. In 2024, the archipelago reached 131.5 thousand visitors, approaching the annual limit of 132 thousand tourists imposed by environmental authorities. The increase reflects the destination's growing popularity, with 11,000 more visitors than the previous year (Cunha, 2025). Additionally, Sánchez et al. (2023) notes that the growth in both tourism and permanent residents (from 2,416 islanders in 1998 to approximately 6,000 in 2021) has contributed to a rising demand for energy and increased environmental impacts.
Given these concerns, effective actions are urgently needed to address visitation and associated infrastructure developments and reduce the negative impacts on key attributes.
Residential Areas, Recreation & Tourism Areas
(Urban growth)
Inside site
, Widespread(15-50%)
Outside site
Housing, commercial development, marine transport infrastructure, major visitor accommodations, and associated infrastructure were identified by the State Party in 2023 as current and substantial external threats to the property (State Party of Brazil, 2023).
Urban development on Fernando de Noronha has resulted in the improper disposal of solid and liquid waste, disturbance and displacement of native species, seabird collisions with aircrafts, and the degradation of scenic values (ICMBio, 2011b; WDPA, 2011). Coral mortality has been observed at both the southwestern and northeastern ends of the north shore, linked to the harbor (northeast) and sewage outfall (southwest) (de Fretias, 2011). Urban growth remains poorly regulated. Between 1991 and 2010, the population of residents increased by approximately 1,000 individuals, not including visitors (Santana et al., 2016). The Management Plan highlights that the environmental preservation area has a demographic density of 290.1 inhabitants per km² within 8 km². If only the areas for residents and visitors are considered, the density could potentially rise to 1,000 inhabitants per km². To avoid the island’s collapse, supporting capacity studies recommend maintaining this population limit (Santana et al., 2016).
In 2016, the Associação de Pousadas reported 86 legally operating hotels on the island. Despite recent tourism development, however, infrastructure is still considered highly inadequate. The carrying capacity study set limits on urban growth, yet the study also led to the emergence of numerous illegal hotels (IUCN Consultation, 2020). Gestão Insular, an authority of the State District of Fernando de Noronha, is linked to the Secretary of Science and Technology and is funded by both the state government and its own resources (e.g., the TPA and TLL). The TPA (Taxa de Preservação Ambiental) is directed towards investments in infrastructure such as waste disposal, healthcare facilities, and nursing services, while the TLL supports the state government, which then redirects the funds to Gestão Insular. These financial resources benefit the local community, funding activities like garbage disposal treatment (sent to the mainland) and road maintenance. Additionally, 70% of the funds generated from entrance fees are reinvested into the park in the form of improved facilities (IUCN Consultation, 2020).
In 2009, a Study on Support Capacity for the implementation of the Management Plan for the Environmental Protection Area, developed by ICMBio, set a limit of 630 land vehicles for Fernando de Noronha. However, data from Detran-PE shows that by 2018, the island's car fleet had grown to 1,369 vehicles, indicating a lack of control over vehicle growth on the island (State Party of Brazil, 2023).
Despite efforts to ensure environmental conservation, significant issues remain in the urban area of Fernando de Noronha, such as inadequate basic sanitation, water treatment, and waste disposal (de Araujo et al., 2018).
Urban development on Fernando de Noronha has resulted in the improper disposal of solid and liquid waste, disturbance and displacement of native species, seabird collisions with aircrafts, and the degradation of scenic values (ICMBio, 2011b; WDPA, 2011). Coral mortality has been observed at both the southwestern and northeastern ends of the north shore, linked to the harbor (northeast) and sewage outfall (southwest) (de Fretias, 2011). Urban growth remains poorly regulated. Between 1991 and 2010, the population of residents increased by approximately 1,000 individuals, not including visitors (Santana et al., 2016). The Management Plan highlights that the environmental preservation area has a demographic density of 290.1 inhabitants per km² within 8 km². If only the areas for residents and visitors are considered, the density could potentially rise to 1,000 inhabitants per km². To avoid the island’s collapse, supporting capacity studies recommend maintaining this population limit (Santana et al., 2016).
In 2016, the Associação de Pousadas reported 86 legally operating hotels on the island. Despite recent tourism development, however, infrastructure is still considered highly inadequate. The carrying capacity study set limits on urban growth, yet the study also led to the emergence of numerous illegal hotels (IUCN Consultation, 2020). Gestão Insular, an authority of the State District of Fernando de Noronha, is linked to the Secretary of Science and Technology and is funded by both the state government and its own resources (e.g., the TPA and TLL). The TPA (Taxa de Preservação Ambiental) is directed towards investments in infrastructure such as waste disposal, healthcare facilities, and nursing services, while the TLL supports the state government, which then redirects the funds to Gestão Insular. These financial resources benefit the local community, funding activities like garbage disposal treatment (sent to the mainland) and road maintenance. Additionally, 70% of the funds generated from entrance fees are reinvested into the park in the form of improved facilities (IUCN Consultation, 2020).
In 2009, a Study on Support Capacity for the implementation of the Management Plan for the Environmental Protection Area, developed by ICMBio, set a limit of 630 land vehicles for Fernando de Noronha. However, data from Detran-PE shows that by 2018, the island's car fleet had grown to 1,369 vehicles, indicating a lack of control over vehicle growth on the island (State Party of Brazil, 2023).
Despite efforts to ensure environmental conservation, significant issues remain in the urban area of Fernando de Noronha, such as inadequate basic sanitation, water treatment, and waste disposal (de Araujo et al., 2018).
To date, there is little evidence of climate change impacting the site’s marine environment, but sea temperature increases, oceanic acidification, and sea-level rise are expected to impact the site in the future. The threat of new species' invasions are perceived as very high due to the lack of both biosecurity to monitor for new invasions and capacity to respond to invasions.
Invasive Non-Native/ Alien Species
(New species invasions)
Inside site
, Throughout(>50%)
New species could be introduced to the main island of Fernanda de Noronha through human activities and connectivity, particularly via the port or airport. These species could have major unforeseen impacts on the biodiversity of the site. Currently there is no biosecurity to monitor for new invasions nor capacity to respond to invasions (IUCN Consultation, 2020). Biosecurity on offshore islets is required to stop species such as cats, rats and tegu arriving at them (Russell and Taylor, 2019). Some species brought to Fernando de Noronha in the past have had a significant impact on the local flora and fauna. The cat preys on native fauna. The jetirana vine suffocates the vegetation and the legume leucena invades the area of the local flora. Vegetation insects and pathogens have also impacted the flora. The lionfish and the heron naturally arrived in recent years and have caused significant changes in Brazilian coast (Luiz et al., 2021).
Changes in Temperature Regimes, Changes in Precipitation & Hydrological Regime
(Climate Change)
Inside site
, Throughout(>50%)
Outside site
Climate change is causing sea temperature increases and ocean acidification, which leads to mortality of oceanic calcifying organisms (ICMBio, 2011b; WDPA, 2011). Some models also suggests that the distribution pattern of marine species could be affected by climate change (Boavida-Portugal et al., 2018). Sea-level rise will impact low-lying Atol das Rocas; however, no specific evidence of this or other changes resulting from severe weather is available, although changes in the regular temperature behaviour were registered in 2015 in the South Atlantic ocean as result of El Niño events. In 2023, it was noted that Climate Change is already affecting the primary productivity and biodiversity of Atol das Rocas and Fernando de Noronha (State Party of Brazil, 2023). Viegas at al. (2021) reported that Fernando de Noronha Archipelago is becoming potentially at risk of climatic and bioclimatic variation due to anthropogenic climate changes. The lack of quantitative and qualitative evaluations of climate change impacts on local biodiversity and human livelihood impair the development of adequate mitigation policies.
Water-borne & other effluent Pollution
(Persistent organic pollution)
Inside site
, Extent of threat not known
The presence and distribution of persistent organic pollutants and contaminants of emerging concern were evaluated in spinner dolphins (Stenella longirostris) from the Fernando de Noronha Archipelago. Combi et al. (2022) found that, although contaminant levels were relatively low, the presence of these chemicals poses an additional stressor to the dolphins, which are already facing increasing anthropogenic pressures—particularly those associated with tourism activities in the region. The contaminant levels observed in this study were significantly lower than those previously reported in spinner dolphin populations from the Indian and Pacific Oceans.
Garbage & Solid Waste
(Plastic pollution)
Inside site
, Extent of threat not known
The Fernando de Noronha Archipelago is highly vulnerable to microplastic pollution, which has been previously detected through snapshot sampling efforts. In 2021, an incident of unknown origin resulted in the arrival of approximately 1.3 tons of plastic and oil on the archipelago’s shores (Magalhães et al., 2020). Carvalho et al. (2021) found that microplastic contamination is recurrent in the area and that its distribution is influenced by a combination of physical processes. Although comparisons with global beach data were made using different concentration units, the lack of standardized sampling and analysis methods hinders a more accurate understanding of the large-scale spatial and temporal variability of microplastics.
Involvement of stakeholders and rightsholders, including indigenous peoples and local communities, in decision-making processes
According to the most recent periodic report (State Party of Brazil, 2023), there is only some participation of key stakeholders in the management system and the relationship between the property managers and local stakeholders is poor. Tensions between tourism and conservation goals sometimes lead to differences, which need addressing in the National Park Consultative Committee, and as part of the participatory process for the development of the property’s management plan (ICMBio, 2011). Environmental NGOs take part in discussions about planning, community capacity-building and monitoring, and act as facilitators (Estima et al., 2013). However, as the majority of tourism-directed decisions are made by the hotel owners, ICMBio and Gestão Insular, people outside of these organizations are not always able to effectively participate in decision-making processes (IUCN Consultation, 2020).
The participatory process in the protected area takes place in the context of advisory councils; however, the final decision is made by the managing institution. A Sustainability Program for the FN Archipelago – Noronha +20, which is an interinstitutional pact aiming at the social and environmental well-being of the archipelago, focuses on critical issues ranging from urban and public use to research, education and health (Programa de sustentabilidad Noronha + 20, 2011). Co-management mechanism processes between local fisheries and biodiversity-related institutions, particularly the PA system, seem counterproductive, as conservation activities are not fully integrated into small-scale fisheries to provide benefits to these communities (Cantareli et al., 2016). The State Party of Brazil (2023) reported that the lack of governance is a situation found both in ICMBio, in the State of Pernambuco, and in the site management of the Fernando de Noronha Environmental Protection Area.
The participatory process in the protected area takes place in the context of advisory councils; however, the final decision is made by the managing institution. A Sustainability Program for the FN Archipelago – Noronha +20, which is an interinstitutional pact aiming at the social and environmental well-being of the archipelago, focuses on critical issues ranging from urban and public use to research, education and health (Programa de sustentabilidad Noronha + 20, 2011). Co-management mechanism processes between local fisheries and biodiversity-related institutions, particularly the PA system, seem counterproductive, as conservation activities are not fully integrated into small-scale fisheries to provide benefits to these communities (Cantareli et al., 2016). The State Party of Brazil (2023) reported that the lack of governance is a situation found both in ICMBio, in the State of Pernambuco, and in the site management of the Fernando de Noronha Environmental Protection Area.
Legal framework
The property has adequate legal protection conferred by a number of federal laws and state regulations. The Chico Mendes Institute for Biodiversity Conservation (ICMBio), an autonomous federal agency under the Ministry of Environment, is responsible for the management and conservation of the site (World Heritage Committee, 2015). The Atol das Rocas Marine Protected Area was established in 1979 and later redesignated as the first National Biological Marine Reserve. In 1988 the Fernando de Noronha Marine National Park was created by Federal Decree 96.693 and in 1989 the entire archipelago and surrounding waters were declared an Environmental Protection Area of the state of Pernambuco by State Decree 13555 which forms the legal basis for the buffer zone around the Marine National Park. Law enforcement is incipient, hampered by lack of resources (IBAMA, 2006).
Governance arrangements
Fernando de Noronha is administratively divided among three main entities: the Government of the State of Pernambuco—through the Administration of the State District of Fernando de Noronha (ADEFN)—the Brazilian Air Force, and ICMBio (Ataíde et al., 2024). The region includes two federal conservation units: the Fernando de Noronha Marine National Park and the Environmental Protection Area of Fernando de Noronha - Rocas - São Pedro and São Paulo. Fioravanso (2020) analyzed environmental governance in the Fernando de Noronha Archipelago and identified two key challenges: the lack of institutional integration and the failure to enforce environmental regulations, both of which contribute significantly to the socio-environmental issues affecting the area. Similarly, in 2023, the State Party of Brazil emphasized the ongoing governance deficiencies within both ICMBio, the site management of the Marine National Park, and the State of Pernambuco. These gaps have hindered effective site inspection and overall management (State Party, 2023). Additionally, collaboration between the World Heritage site managers and other stakeholders has been consistently reported as weak, further limiting the effectiveness of conservation and management efforts.
Integration into local, regional and national planning systems (including sea/landscape connectivity)
An overall framework for integration into national and state protected areas systems and tourism development activities exists (ICMBio, 2011b). However, in practice comprehensive integrated management could be improved (IUCN Consultation, 2014).
Boundaries
At the time of inscription, the boundaries of the property were deemed "adequate for conserving marine biodiversity" (IUCN, 2001), and it was noted that all key terrestrial habitats were included within the property. However, concerns have been raised regarding the level of awareness among the local population about the site's World Heritage status and its boundaries (IUCN Consultation, 2014). In the 2023 periodic report the State Party indicated that the Fernando de Noronha and Atol das Rocas Reserves cover a total area of 42,270 hectares, with a buffer zone of 140,713 hectares. In 2023, the State Party considers the site's boundaries and buffer zone to be appropriate for the conservation of marine biological diversity and states they do not limit the ability to maintain the property’s Outstanding Universal Value (OUV), even though the property is divided into two separate components (State Party of Brazil, 2023).
Overlapping international designations
In 2015, 35,186 hectares of the Atol das Rocas Reserves were designated as a Ramsar site, followed by 10,929 hectares of the Fernando de Noronha Archipelago in 2018. The extent to which this is integrated in the management of the World Heritage site could not be assessed comprehensively. Additionally, both areas were incorporated into the World Network of Biosphere Reserves, as thei overlap with the Atlantic Forest Biosphere reserve. Regarding the Geopark program, the area is not currently included; however, there are plans to promote its inclusion within the next three years (State Party of Brazil, 2023). Additionally, the Fernando de Noronha archipelago is one of the key areas for biodiversity conservation on the Brazilian coast.
Implementation of World Heritage Committee decisions and recommendations
No Committee decisions have been taken since inscription of the property.
Climate action
In Brazil, the enactment of Law No. 12.187 on December 29, 2009, which established the National Policy on Climate Change, has played a key role in advancing efforts to understand the nature, intensity, and frequency of climate change impacts. This law, along with the National Adaptation Plan introduced in 2021, aims to identify vulnerable populations and implement targeted adaptation and mitigation strategies. A study by Monteiro et al. (2021) assessed the vulnerability of the population of Fernando de Noronha using the Municipal Vulnerability Index developed by the Oswaldo Cruz Foundation, census data from the Brazilian Institute of Geography and Statistics (IBGE), and geospatial analysis of high-resolution satellite imagery processed through specialized software. The study concluded that the population exhibits a medium level of vulnerability. Although Brazil has developed an Adaptation National Plan, the coastal management framework and primarily port planning there remains a need to improve implementation and institutionalisation (Lima & de Souza, 2022). Furthermore, there is limited evidence available regarding the specific impacts of climate change on World Heritage property and relevant site level management responses.
Management plan and overall management system
Fernando de Noronha National Park, Rocas Biological Reserve and the surrounding Environmental Protection Area are understaffed and underfunded, which hampers efficient law enforcement (IUCN Consultation, 2014). The Atol das Rocas Biological Reserve is banned from public access and managed for the protection of species and for research. The Reserve benefits from surveillance by the Brazilian Navy and the Air Force, notably as concerns fishing and tourism activities, while the National Parks has a Sustainable Development and Ecotourism Management Plan, strictly controlling the development of tourism infrastructure and visits (World Heritage Committee, 2015). The updating of the management plans (Santana et al., 2016; ICMBio, 2017) suggests adequate responses are being proposed by the protected area (PA) authority to face the new challenges to control illegal activities and reinforce management. EcoNoronha, ICMBio and Gestão Insular imposes fees on tourists and, therefore, influence their behaviour due to intense monitoring. Migration control for tourists, residents and temporary workers is mandatory in the airport and port. These measures work in practice because the aforementioned actors hold the discourse of environmental conservation and carrying capacity that is subsided by research. The redistribution of those payments for ecosystem services are invested in environmental protection posing as incentive for people to pay the entrance fee and TPA (IUCN Consultation, 2020). The Fernando de Noronha National Marine Park has fenced-off beaches where visitors must show their previously paid “visitor card”, valid for ten days, in the PICs (control posts), where it is checked electronically in order to be granted access to these specific beaches within the park (de Araujo et al., 2018). Currently, the two sites have well-developed but separate management plans, both of which address key issues such as tourism, scientific research, environmental education, and the protection and monitoring of biodiversity. However, according to the State Party the Sustainable Development and Ecotourism Management Plan, built with the support of the local population, was not implemented. These plans were supported by complementary studies—including Noronha +20, the Carrying Capacity Studies for Fernando de Noronha, and the Ecotourism Management Plan—all developed with input from the local community (State Party of Brazil, 2023). However, the lack of implementation has led to negative impacts on both protected areas, with direct consequences for the Fernando de Noronha National Marine Park (State Party of Brazil, 2023). In response, preparatory meetings for the revision of the Management Plan for the Environmental Protection Area (APA) of Fernando de Noronha began in January 2024, marked by strong public participation.
Law enforcement
Law enforcement efforts remain limited due to a lack of resources (IBAMA, 2006). However, recent progress has been made in strengthening the legal framework. Notably, Ordinance No. 242 of April 2021 and Ordinance No. 1,275 of December 2022 introduced important updates to the Management Plan of the Environmental Protection Area (APA) of Fernando de Noronha – Rocas – São Pedro and São Paulo.
Sustainable finance
While 70% of the entrance fees go back to management of the park, finance was considered in 2012 as inadequate to manage the site as outlined in the management plans (ICMBio, 2012). In 2023, the State Party reported three main funding sources for the World Heritage property: multilateral funding, national or federal government support, and commercial activities. International donations accounted for 15% of the operating costs but were not allocated to project expenses. The available budget is considered acceptable and secure over the medium term, however it could be improved to fully meet management needs (State Party of Brazil, 2023). Payment for ecosystem services schemes in Fernando de Noronha are valuable for preserving ecosystem services through ecotourism in protected areas if the revenues are re-invested into the preservation of the site, which is the case with the Fernando de Noronha National Marine Park (de Araujo, 2018).
Staff capacity, training and development
The EPA management plan includes a capacity-building program aimed at environmental guides and the local population to improve tourism management and other activities for both management and technical staff (ICMBio, 2017). ICMBio currently runs ACADEBIO, a state-owned academy designed to strengthen the capacities of all Chico Mendes staff across the country. ICMBio, a government-based organization established in 2007, is responsible for managing federal protected areas in Brazil, including the Fernando de Noronha National Marine Park and the Fernando de Noronha Protected Area. Funded by both the federal and state governments, ICMBio had 50 employees and 8 volunteers working on Fernando de Noronha in 2016 (de Araujo et al., 2018). In 2023, the State Party noted that the presence of trained human resources positively impacts management activities but the availability of most training opportunities is still poor (State Party of Brazil, 2023).
Education and interpretation programmes
Sporadic educational activities are carried out, but the awareness among local people of the World Heritage status of the property is low (IUCN Consultation, 2014). Environmental NGOs participate in tourism discussions to guide measures and monitoring with local communities (Estima et al., 2013). The current management plan has an education and interpretation program (ICMBio, 2017), but its effectiveness is still to be assessed. In 2023, State Party noted that there is a limited and ad hoc education and awareness programme currently implemented at the property (State Party of Brazil, 2023).
The Tamar Project Visitor Center offers free talks each evening to create awareness in visitors and the community. The educational topics are sharks, sea turtles, dolphins, National Park, ecotourism, and others. The area also hosts the Sea Turtle Outdoor Museum, with life-size fiberglass replicas of the five species of sea turtles found in Brazil. As an interpretive, educational environment and local development provider, the Visitor Center and the Museum are now part of the tourism product of Fernando de Noronha.
Another of the island’s educational offerings is the Shark Museum, where a series of interpretive signs discuss wave patterns and ocean currents and their role on the island. The Noronha Memorial “Américo Vespúcio Cultural Space” also includes educational interpretive signage focusing on geologic and geomorphologic aspects of the archipelago (Moreira et al. 2021).
Centro Golfinho Rotador is an NGO that was created to protect the Rotador Dolphin, but has extended its efforts towards environmental conservation as a whole and has also focused on social welfare. Centro Golfinho Rotador is funded by donations from both public and private institutions (IUCN Consultation, 2020). Centro TAMAR is a cooperation between a government agency and a non-government-based institution with 22 bases throughout Brazil aiming at conserving endangered marine turtle species. Their main action towards tourism is the Ecotourism Program, which consists of three initiatives: 1. Assisted intentional capture: tourists can watch turtles being safely captured every Monday and Thursday. 2. Tartarugada: monitoring of Leão Beach to mark nests and female turtles. Only four people can participate in this initiative due to small living quarters. 3. Nest opening: baby marine turtles release (de Araujo et al., 2018). There is also Noronha + 20, a 20-year program built with civil society, the production sector and the government aimed at preventing environmental degradation in the Archipelago. The environmental protection area has helped making human presence and nature conservation more compatible, contributing to environmental education through direct contact with different forms of life and the interaction with nature (Santana et al., 2016).
The Tamar Project Visitor Center offers free talks each evening to create awareness in visitors and the community. The educational topics are sharks, sea turtles, dolphins, National Park, ecotourism, and others. The area also hosts the Sea Turtle Outdoor Museum, with life-size fiberglass replicas of the five species of sea turtles found in Brazil. As an interpretive, educational environment and local development provider, the Visitor Center and the Museum are now part of the tourism product of Fernando de Noronha.
Another of the island’s educational offerings is the Shark Museum, where a series of interpretive signs discuss wave patterns and ocean currents and their role on the island. The Noronha Memorial “Américo Vespúcio Cultural Space” also includes educational interpretive signage focusing on geologic and geomorphologic aspects of the archipelago (Moreira et al. 2021).
Centro Golfinho Rotador is an NGO that was created to protect the Rotador Dolphin, but has extended its efforts towards environmental conservation as a whole and has also focused on social welfare. Centro Golfinho Rotador is funded by donations from both public and private institutions (IUCN Consultation, 2020). Centro TAMAR is a cooperation between a government agency and a non-government-based institution with 22 bases throughout Brazil aiming at conserving endangered marine turtle species. Their main action towards tourism is the Ecotourism Program, which consists of three initiatives: 1. Assisted intentional capture: tourists can watch turtles being safely captured every Monday and Thursday. 2. Tartarugada: monitoring of Leão Beach to mark nests and female turtles. Only four people can participate in this initiative due to small living quarters. 3. Nest opening: baby marine turtles release (de Araujo et al., 2018). There is also Noronha + 20, a 20-year program built with civil society, the production sector and the government aimed at preventing environmental degradation in the Archipelago. The environmental protection area has helped making human presence and nature conservation more compatible, contributing to environmental education through direct contact with different forms of life and the interaction with nature (Santana et al., 2016).
Tourism and visitation management
Fernando de Noronha is administratively divided among the Government of the State of Pernambuco—through the Administration of the State District of Fernando de Noronha (ADEFN)—the Brazilian Air Force, and ICMBio (Ataíde & Lins, 2024). This site offers a well-developed network of trails guided by trained local experts, along with recreational activities such as horseback riding, fishing, and boat tours. Dolphin watching is particularly popular among visitors. The National Park features an interpretive center at its headquarters, where environmental education talks are held regularly (UNEP-WCMC, 2011).
However, there is some concern that the current tourism model is unsustainable and inappropriate for the island, and that a shift toward an ecotourism-based approach is needed to ensure the conservation of the property's OUV.
Fernando de Noronha has conducted carrying capacity study and developed sustainable tourism infrastructure that supports a high-quality visitor experience while prioritizing environmental preservation. Despite these efforts, the number of visitors continues to rise. Both Gestão Insular and EcoNoronha have acknowledged the problem: the number of annual visitors increased from 90,000 in 2015 to over 106,000 in 2019, and according to the annual flow chart publicly available from the Island's Administration, the site received 114,106 tourists in 2021 (Ataíde & Lins, 2024). This far exceeds the management plan’s optimal limit of 89,000 tourists per year (Marinho, 2020). Illegal accommodation and unauthorized tourist entries also remain issues that require strict monitoring and enforcement (de Araujo, 2018). ICMBio Transparency data (https://www.parnanoronha.com.br/en/transparencia) indicates that the Fernando de Noronha Marine National Park received 131,503 visitors in 2024. The Sustainable Development and Ecotourism Management Plan—although initially developed with local community support—was ultimately not implemented (State Party of Brazil, 2023). Consequently, tourism infrastructure expanded uncontrollably in urbanized areas outside the park boundaries, resulting in violations of the carrying capacity in several parts of the Fernando de Noronha National Marine Park. In contrast, the conservation status of the Atol das Rocas ecosystems has improved. Predatory fishing and the illegal presence of tourist boats no longer pose significant threats to their ecological integrity (State Party of Brazil, 2023).
The annual increase in the number of tourists has impacted the island’s environment, which has encouraged authorities to establish visitation limits and an admission fee per day, called “environmental preservation fee (Taxa de Preservação Ambiental – TPA)”. The fee is paid to the federal government of Pernambuco and is then returned to Gestão Insular, who decides where to invest the money. To provide ecotourism services to the public, an entrance fee was established to allow entrance to specific areas of the Fernando de Noronha National Marine Park for up to 10 consecutive days. Both the TPA and the entrance fee are mandatory for visitors to the island. Although the fees are expensive considering the cost of living in Brazil, visitation numbers have increased since their establishment (de Araujo et al., 2018).
Both terrestrial and marine carrying capacities may needs to be reviewed and updated due to the unregulated growth of tourism, the expansion of lodging facilities without adequate sanitation, increasing erosion and degradation of drainage systems and watersheds, and the broader deterioration of natural ecosystems. These factors are compromising the ecosystem’s ability to sustain species and withstand environmental disturbances.
However, there is some concern that the current tourism model is unsustainable and inappropriate for the island, and that a shift toward an ecotourism-based approach is needed to ensure the conservation of the property's OUV.
Fernando de Noronha has conducted carrying capacity study and developed sustainable tourism infrastructure that supports a high-quality visitor experience while prioritizing environmental preservation. Despite these efforts, the number of visitors continues to rise. Both Gestão Insular and EcoNoronha have acknowledged the problem: the number of annual visitors increased from 90,000 in 2015 to over 106,000 in 2019, and according to the annual flow chart publicly available from the Island's Administration, the site received 114,106 tourists in 2021 (Ataíde & Lins, 2024). This far exceeds the management plan’s optimal limit of 89,000 tourists per year (Marinho, 2020). Illegal accommodation and unauthorized tourist entries also remain issues that require strict monitoring and enforcement (de Araujo, 2018). ICMBio Transparency data (https://www.parnanoronha.com.br/en/transparencia) indicates that the Fernando de Noronha Marine National Park received 131,503 visitors in 2024. The Sustainable Development and Ecotourism Management Plan—although initially developed with local community support—was ultimately not implemented (State Party of Brazil, 2023). Consequently, tourism infrastructure expanded uncontrollably in urbanized areas outside the park boundaries, resulting in violations of the carrying capacity in several parts of the Fernando de Noronha National Marine Park. In contrast, the conservation status of the Atol das Rocas ecosystems has improved. Predatory fishing and the illegal presence of tourist boats no longer pose significant threats to their ecological integrity (State Party of Brazil, 2023).
The annual increase in the number of tourists has impacted the island’s environment, which has encouraged authorities to establish visitation limits and an admission fee per day, called “environmental preservation fee (Taxa de Preservação Ambiental – TPA)”. The fee is paid to the federal government of Pernambuco and is then returned to Gestão Insular, who decides where to invest the money. To provide ecotourism services to the public, an entrance fee was established to allow entrance to specific areas of the Fernando de Noronha National Marine Park for up to 10 consecutive days. Both the TPA and the entrance fee are mandatory for visitors to the island. Although the fees are expensive considering the cost of living in Brazil, visitation numbers have increased since their establishment (de Araujo et al., 2018).
Both terrestrial and marine carrying capacities may needs to be reviewed and updated due to the unregulated growth of tourism, the expansion of lodging facilities without adequate sanitation, increasing erosion and degradation of drainage systems and watersheds, and the broader deterioration of natural ecosystems. These factors are compromising the ecosystem’s ability to sustain species and withstand environmental disturbances.
Sustainable use
Lobster fishing is allowed in the Sustainable Fishing Zone of the environmental protection area, but no information is available regarding whether it can be considered sustainable. Tourism as mentioned above poses a key threat to the OUV and requires more effective management.
Monitoring
In 2023, the development of low-impact research and monitoring were identified as positive aspects of the site, compared to the reality of other Conservation Units in Brazil (State Party of Brazil, 2023). According to the information provided by the State Party, there is a comprehensive and integrated monitoring program that addresses management needs and enhances understanding of the site’s Outstanding Universal Value. However, there are gaps in the indicators used and in stakeholder participation in the monitoring activities (State Party of Brazil, 2023).
A comprehensive monitoring system has not been developed for the entire World Heritage site. However, the Brazilian National Reef Monitoring Program has monitored coral coverage and condition in the property since 2002 (Rodriguez-Ramiriz et al., 2008). Plans were underway to develop a specific monitoring system for recreational diving in order to reduce damage to coral communities (Luiz, 2012), however the current status of this is unclear. Fishing data indicate the need to elaborate a joint resource management plan that results in the valuation of the artisanal fisherman and the sustainability of the fishing activity, including a monitoring strategy (Domínguez et al., 2015). The Noronha +20 Sustainability Observatory is a proposal of management and monitoring instruments to follow up actions in the management plan, organize and collect information and disseminate actions and results (Programa de sustentabilidad Noronha + 20, 2011).
A comprehensive monitoring system has not been developed for the entire World Heritage site. However, the Brazilian National Reef Monitoring Program has monitored coral coverage and condition in the property since 2002 (Rodriguez-Ramiriz et al., 2008). Plans were underway to develop a specific monitoring system for recreational diving in order to reduce damage to coral communities (Luiz, 2012), however the current status of this is unclear. Fishing data indicate the need to elaborate a joint resource management plan that results in the valuation of the artisanal fisherman and the sustainability of the fishing activity, including a monitoring strategy (Domínguez et al., 2015). The Noronha +20 Sustainability Observatory is a proposal of management and monitoring instruments to follow up actions in the management plan, organize and collect information and disseminate actions and results (Programa de sustentabilidad Noronha + 20, 2011).
Research
Since the 1970s, the Federal government has organised scientific expeditions and research today is regularly conducted, particularly on spinner dolphins (Project GOLFINHO ROTADOR) and nesting marine turtle populations (Project TAMAR) on Fernando de Noronha, where the main nesting beaches of the green turtle have been monitored since 1987. These projects are however highly dependent on external funding from PETROBRAS National Oil Company and other sources. On the Atol das Rocas regular studies have been conducted since 1990 on migratory and resident seabirds, as well as on migrating hawksbill turtles, fish, crustaceans, coralline algae and benthic organisms (WDPA, 2011). Long-term research on reef fishes has received more attention in the recent years, as a means for evaluating overfishing effects and for comparing pristine vs coastal areas under urban impacts (MCTI/CNPq, 2012). Research facilities have been developed on Fernando de Noronha (TAMAR Project since 1984), Atol das Rocas (University of North Rio Grande since 1991), and in the Sao Pedro e Sao Paulo Archipelago (since 1998) (ICMBio, 2011b). Several projects have been led by the ICMBio and research institutions e.g. sharks project on participatory monitoring (Gracía y Clapis, 2008), the Tamar Project for marine turtles and the Spinner Dolphin Project (World Heritage Committee, 2015; Mohr et al., 2009). Recently established partnerships among governmental executive bodies, NGO’s, research institutes and universities have promoted the development of research and management of invasive species on the archipelago (Micheletti et al., 2020).
In addition to the TPA and entrance fees, and to further support local wildlife management, ICMBio has developed two key projects: the Tamar-ICMBio Project—an internationally recognized marine conservation initiative that actively involves coastal communities in socio-ecological research and conservation activities—and the Spinner Dolphin Project, which focuses on the preservation of spinner dolphins in the Fernando de Noronha Archipelago. The latter is carried out by the NGO Spinner Dolphin Center and officially sponsored by Petrobras through its Social and Environmental Program.
In addition to the TPA and entrance fees, and to further support local wildlife management, ICMBio has developed two key projects: the Tamar-ICMBio Project—an internationally recognized marine conservation initiative that actively involves coastal communities in socio-ecological research and conservation activities—and the Spinner Dolphin Project, which focuses on the preservation of spinner dolphins in the Fernando de Noronha Archipelago. The latter is carried out by the NGO Spinner Dolphin Center and officially sponsored by Petrobras through its Social and Environmental Program.
Effectiveness of management system and governance in addressing threats outside the site
Threats originating outside the property include inappropriate tourism development, urban growth in the town of Vila dos Remedios on Fernando de Noronha, novel invasive species and climate change. Environmental impacts from cruise tourism need to be further investigated. The current management system is not fully effective at mitigating these threats, in part due to lacking cooperation between site management, local authorities and other local stakeholders and the lack of implementation of plans, also due to lacking resources.
Effectiveness of management system and governance in addressing threats inside the site
The Fernando de Noronha Archipelago National Marine Park, the Atol das Rocas Marine Biological Reserve and the Environmental Protection Area (APA) are administered by the Chico Mendes Biodiversity Conservation Institute (ICMBio). Management Plans were prepared by ICMBio for the Atol das Rocas Marine Biological Reserve in 2007 and for the Fernando de Noronha APA and National Marine Park in 2011 and address issues such as tourism, research, environmental education, protection and monitoring of the biodiversity. For the environmental protection area, the management plan was updated and singed in June 2017 (ICMBio, 2017).
The advisory councils of the Fernando de Noronha National Marine Park and the Fernando de Noronha Environmental Protected Area holds six meetings annually. Residents tend to be more involved in meetings related to the protected area because these are focused on the urban area of the island. ICMBio has made efforts to establish a participative management program through the advisory councils, but most of the residents leave the decisions to their “leaders” claiming their requests were never accepted. The dominant groups tend to have their own discourse and, because they are in a position of power, this speech becomes official, acting as true for the rest of the community. The less powerful actors in this context have no priority in the interests of more powerful actors and often have no means to fight for more support. Thus, the interests of minority groups are not popular, they do not become public and are not discussed as a possibility (de Araujo et al., 2018). In 2023, the State Party mentioned that the Sustainable Development and Ecotourism Management Plan—originally developed with support from the local population—was not implemented. As a result, tourist and visitation infrastructure expanded uncontrollably in urbanized areas outside the property, leading to non-compliance with the carrying capacity in various parts of the Fernando de Noronha National Marine Park. In contrast, the preservation level of the ecosystems in Atol das Rocas has improved, with predatory fishing and the illegal presence of tourist boats no longer representing major threats to the site's integrity. The marine ecosystems, endangered species and the spinner dolphin key attributes nevertheless are considered seriously compromised (State Party of Brazil, 2023).
The advisory councils of the Fernando de Noronha National Marine Park and the Fernando de Noronha Environmental Protected Area holds six meetings annually. Residents tend to be more involved in meetings related to the protected area because these are focused on the urban area of the island. ICMBio has made efforts to establish a participative management program through the advisory councils, but most of the residents leave the decisions to their “leaders” claiming their requests were never accepted. The dominant groups tend to have their own discourse and, because they are in a position of power, this speech becomes official, acting as true for the rest of the community. The less powerful actors in this context have no priority in the interests of more powerful actors and often have no means to fight for more support. Thus, the interests of minority groups are not popular, they do not become public and are not discussed as a possibility (de Araujo et al., 2018). In 2023, the State Party mentioned that the Sustainable Development and Ecotourism Management Plan—originally developed with support from the local population—was not implemented. As a result, tourist and visitation infrastructure expanded uncontrollably in urbanized areas outside the property, leading to non-compliance with the carrying capacity in various parts of the Fernando de Noronha National Marine Park. In contrast, the preservation level of the ecosystems in Atol das Rocas has improved, with predatory fishing and the illegal presence of tourist boats no longer representing major threats to the site's integrity. The marine ecosystems, endangered species and the spinner dolphin key attributes nevertheless are considered seriously compromised (State Party of Brazil, 2023).
While management instruments and legal provisions are in place to secure protection of the site’s values, lack of effective implementation of tourism control measures, a monitoring system, biosecurity measures and limited resources to undertake new capacity research studies may be compromising the integrity of the property. There are many external actors with interests in the archipelago, including those who exercise power through other institutions. Each player has different interests regarding the development of tourism; generally, however, the interests of the most powerful actors end up driving this development, to the detriment of the interests of local communities, which are typically the most economically and socially vulnerable. At Fernando de Noronha, the ecosystem maintains a high level of integrity, despite the increasing number of visitors and the impacts caused by invasive alien species, however to ensure the conservation in the long term, management effectiveness needs to be further improved. Reports that key plans like the Sustainable Development and Ecotourism Management Plan were not implemented is of some concern.
Good practice examples
To provide financial support and strengthen local wildlife management, ICMBio has the support of some key partners, such as: Projeto Tamar, for sea turtles; Rotator Dolphin Project, for cetaceans and sustainable development; CEMAVE, for the study and conservation of avifauna; AMPARA, to control the cat population.
Spectacular seascape and the highest known population of resident dolphins
Low Concern
Trend
Data Deficient
The scenic values and values associated with outstanding natural phenomenon have been relatively well preserved. Although spinner dolphins are still present in high numbers, there has been distribution changes noted which could be at least partially attributed to tourism pressure (IUCN Consultation, 2014). Between 1991 and 2019, an average of 351 (SD=284) spinner dolphins were recorded on 92% of the days of the year, mainly in Baía dos Golfinhos and in the Baía de Santo Antônio/Entre Ilhas complex. The number of spinners that came on average each year did not show significant variation, but the length of stay and the frequency with which they come to Baía dos Golfinhos changed during this period (Júnior & Silva, 2020). This change of permanence behaviour has been attributed in part to tourism growth (Tischer et al., 2017). The current population trend could not be assessed, however according to IUCN-MMPATF (2023) at Fernando de Noronha Archipelago, large concentrations of spinner dolphins of up to ca. 2000 individuals are recorded throughout the year at the cove known as Dolphins’ Bay. The number of spinners observed average around 300 per day, with a maximum of about 2700 in a single day. In 2022 a study recorded 12,986 interactions between boats and dolphins in the region of Santo Antônio Bay and Entre Ilhas, and more than 88% of these interactions involved some type of inappropriate manouver, such as vessels entering directly into the middle of the group and fragmenting its formation. These interferences affect the animals' movement pattern, alter their routine and compromise their rest (Cunha, 2025).
A key role in the process of reproduction, dispersal and colonisation by marine organisms in the entire Tropical South Atlantic
Low Concern
Trend
Stable
Marine ecological processes within the site have until now been relatively unaffected, though climate change may have major impacts in the future. There is a long history of major human impacts on terrestrial ecosystem processes on Fernando de Noronha since the 19th century, but little impact on the Atol das Rocas.
Marine biodiversity and endangered species of Southern Atlantic
High Concern
Trend
Stable
Fernando de Noronha and Atol das Rocas encompass approximately 10 km² of reef areas, representing 0.8% of the total reef area within the Brazilian region (Souter et al., 2020). While populations of many species remain stable, poorly regulated fishing in the surrounding waters poses significant threats, particularly to shark populations, and may facilitate the introduction of exotic species (IUCN Consultation, 2014; Gaeta et al., 2015; ICMBio, 2017). In addition to increased fishing pressure, other stressors such as marine debris, microplastics, and the effects of climate change—including sea level rise, ocean acidification, and warming, which lead to species range shifts—underscore the urgent need for a more integrated management approach through large-scale marine spatial planning (de Oliveira Soares, 2018). Localized coral mortality has been observed on both the southwestern and northeastern ends of Fernando de Noronha’s northern shore. These occurrences are linked to specific anthropogenic pressures, such as the harbor area in the northeast and a sewage outfall in the southwest (de Freitas, 2011). Moreover, Gurgel (2023) highlights that invasive species, coastal erosion, and tourism activities are contributing factors to the increasing frequency and intensity of coral bleaching events in the archipelago. Souter et al. (2020) also reported a gradual decline in average hard coral cover, accompanied by an increase in algal cover, particularly over the last decade.
Largest concentration of tropical seabirds in the Western Atlantic Ocean
High Concern
Trend
Data Deficient
The site lies within a WWF Global 200 Eco-region and a BirdLife-designated Endemic Bird Area (UNEP-WCMC, 2011).
Fernando de Noronha holds the greatest richness of seabirds in the Brazil, being an important area of breeding and feeding; however, little information is available about breeding biology and movements for most of the species (Gouvêa & Mello, 2017).
The population trends of most of the 11 breeding seabirds on Fernando de Noronha remain unknown, but for three species - White-tailed Tropicbird, Red-footed Booby and White Tern - the population trend has been determined as stable (Mancini et al., 2016). There are, however, some seabird populations identified as high value for the Atlantic going extinct within the site, particularly on Fernando de Noronha, with only a few individuals left, e.g. Red Billed Tropicbirds and Masked Boobies. The Audubon’s Shearwater remains critically endangered and not sufficiently monitored nor protected (Mancini et al., 2016; IUCN Consultation, 2020). On Atol das Rocas, three of the five breeding populations of seabirds are assessed as decreasing (Mancini et al., 2016). In Fernando de Noronha, potential egg and chick predators include exotic and invasive species such as the tegu lizard, rats, cats, and dogs, as well as others that destroy the vegetation, such as the rock cavy, house mice and goats. Another growing threat to these birds is tourism, plastic ingestion and oil pollution (Mancini et al., 2016).
Management actions and eradication of invasive species are urgent and essential for the future conservation of species of avifauna of the Fernando de Noronha Archipelago (Gouvêa & Mello, 2017). In 2024, the number of active nests and breeding adults of the Red-footed Booby (Sula sula) in the Fernando de Noronha Archipelago remained stable compared to the period from 2018 to 2024. While the site continues to serve as an important stopover for migratory species there is a lack of sufficient survey data to establish reliable population trends (Santos et al., 2024).
Fernando de Noronha holds the greatest richness of seabirds in the Brazil, being an important area of breeding and feeding; however, little information is available about breeding biology and movements for most of the species (Gouvêa & Mello, 2017).
The population trends of most of the 11 breeding seabirds on Fernando de Noronha remain unknown, but for three species - White-tailed Tropicbird, Red-footed Booby and White Tern - the population trend has been determined as stable (Mancini et al., 2016). There are, however, some seabird populations identified as high value for the Atlantic going extinct within the site, particularly on Fernando de Noronha, with only a few individuals left, e.g. Red Billed Tropicbirds and Masked Boobies. The Audubon’s Shearwater remains critically endangered and not sufficiently monitored nor protected (Mancini et al., 2016; IUCN Consultation, 2020). On Atol das Rocas, three of the five breeding populations of seabirds are assessed as decreasing (Mancini et al., 2016). In Fernando de Noronha, potential egg and chick predators include exotic and invasive species such as the tegu lizard, rats, cats, and dogs, as well as others that destroy the vegetation, such as the rock cavy, house mice and goats. Another growing threat to these birds is tourism, plastic ingestion and oil pollution (Mancini et al., 2016).
Management actions and eradication of invasive species are urgent and essential for the future conservation of species of avifauna of the Fernando de Noronha Archipelago (Gouvêa & Mello, 2017). In 2024, the number of active nests and breeding adults of the Red-footed Booby (Sula sula) in the Fernando de Noronha Archipelago remained stable compared to the period from 2018 to 2024. While the site continues to serve as an important stopover for migratory species there is a lack of sufficient survey data to establish reliable population trends (Santos et al., 2024).
Only remaining sample of the Insular Atlantic Forest
High Concern
Trend
Stable
Clearing of vegetation and introduced species have had a significant impact within the site on Fernando de Noronha (ICMBio, 2011b; UNEP-WCMC, 2011). Urban growth is poorly regulated and development has led to the dumping of solid and liquid wastes, disturbance and displacement of native species, seabird collisions with aircraft (ICMBio, 2011b; WDPA, 2011). Since its discovery and colonization, Fernando de Noronha native terrestrial species have been impacted by the arrival of several exotic and invasive species, especially domestic cats and dogs, brown and black rats, house mice, cururu-toad (Rhinella jimi), tegu lizard (Salvator merianae), little fire ant (Wasmannia auropunctata), rock cavy (Kerodon rupestris), river tamarind (Leucaena leucocephala) and the lantana (Lantana camara); including several zoonotic diseases, like salmonellosis and toxoplasmosis, linked to some of these species (Micheletti et al., 2020). Several research projects supporting management plans of invasive species are undertaken in order to control effects on e.g. native flora, amphibians, reptiles and birds (Russell et al., 2018; Abrahão et al., 2019).
Assessment of the current state and trend of World Heritage values
Stable
Marine ecological processes within the site have until now been relatively unaffected, though climate change may have major impacts in the future. There is a long history of major human impacts on terrestrial ecosystem processes on Fernando de Noronha since the 19th century, but little impact on the Atol das Rocas. Industrial fishing in the vicinity of the site is, however, impacting on pelagic species in general and sharks in particular and large aggregation of boats have resulted in the introduction of exotic species, causing a potentially significant impact on the marine ecosystem stability of the site. Introduced exotic and invasive species are also having an impact on the native terrestrial flora and fauna of Fernando de Noronha, as well as on breeding seabirds, which appear in long-term decline, however lacking data make a comprehensive assessment difficult. Increasing tourism is having direct negative impacts on key attributes, for example innapropriate vessel movements are impacting spinner dolphin behaviour and movement patterns.
Additional information
Outdoor recreation and tourism
In 2019, over 106,000 tourist visited the property. There is a good network of trails with well-trained local guides and there are riding, fishing and boat rides. Dolphin viewing is very popular. However, an eco-tourism model is needed to assure conservation of the property’s OUV. Tourism is the driver of the economy of Fernando de Noronha. Revenue from tourism are also raising funds for conservation initiatives.
Uncontrolled tourism. Urbanization. Land use change: Increasing number of hotel, deficient urban infrastructure, insufficient provision of water. Over exploitation: Conflict of interests regarding tourism development options on the part of stakeholders.
Contribution to education
ICMBio, Golfinho Rotador and TAMAR provide opportunities for environmental education through guided visitation, lectures, demonstrations and various actions throughout the island. Local schools provide environmental conservation activities for students and community (de Araujo, 2018).
Carbon sequestration,
Soil stabilisation,
Coastal protection
Enviromental services associated to conservation of habitats and species, and coastal protection.
Climate change, land use change due to uncontrolled tourism and urbanization will potentially reduce ecosystem services provided.
Provision of jobs,
Tourism-related income
A range of tourism activities and fisheries.
Uncontrolled tourism and limited participation of local community in management and decision making.
At the national and global level, conservation is the main benefit of the property, while on the island of Fernando de Noronha, tourism is considered the main benefit of the property.
| № | Organization | Brief description of Active Projects | Website |
|---|---|---|---|
| 1 | Dr. Beatrice Padovani Ferreira, Departamento de Oceanografia, Universidade Federal de Pernambuco | RC Brazil has received funding from PROBIO, a division of the Brazilian Ministry of Environment, to monitor the 3,000 km of reef along the Northeastern coast. Four pilot locations have been selected: Abrolhos Reef, Fernando de Noronha Archipelago, the Coral Coast MPA and the Maracajaú Reefs. |
https://www.reefcheck.org/country/brazil/
|
| 2 | Institutions supporting the monitoring/survey efforts: Atol das Rocas-ICMBIO; Noronha-ICMBIO and Atlantis Divers; | Started in 2002, and includes all major reef areas in Brazil, including Fernado de Noronha and Atol da Rocas (Rodriguez-Ramirez et al., 2008). |
https://icriforum.org/members/brazil/#:~:text=The%20Brazilian%20National%20Coral%20Reef,to%20characteristics%20of%20Brazilian%20reefs.
|
| 3 | Dr. José Martins da Silva Jr., Ph.D., Spinner Dolphin Center | Research on the spinner dolphin, provision of visitor information on the species, advice for conservation policies and efforts towards achieving sustainability for human activities at Fernando de Noronha. |
https://golfinhorotador.org.br/en/sobre-nos/o-projeto/
|
| 4 | Project TAMAR | Research and protection of nesting marine turtle populations on Fernando de Noronha. Maintenance of a visitor center with facilities for environment-related lectures and events used by several other institutions on a regular basis. |
https://www.tamar.org.br/
|
| 5 | Conservation Leadership Programme. José Garcia Júnior – Project Leader Ricardo Clapis Garla – Co-leader | Capacitate the fishermen for to implement a participative fisheries monitoring in Fernando de Noronha Archipelago and to incorporate the local community as the main agent of the shark management program. |
https://www.conservationleadershipprogramme.org/project/fernando-de-noronha-shark-project-brazil/
|
| 6 | Carlos Roberto Abrahão, Paulo Rogerio Mangini, Jean Carlos Ramos Silva e Ricardo Augusto Dias | Understand the sanitary situation state of teiús populations in FN and their interference in the health of the ecosystem. | |
| 7 | Vinicius Gasparotto, Paulo Rogerio Mangini e Ricardo Augusto Dias | Risk analysis to health of the mabuias populations posed by introduced species mainly the lagarto lizzard, in the Fernando de Noronha island. Impacts of feral cats. | |
| 8 | Tatiane Micheletti e Paulo Rogerio Mangini. | (I) access the dynamic structure of the moco pupulation (II) their general health condition (III) understand the relation between the residents and tourists of the Island and the species (IV) identify dietary components (V) identify costs and benefits of different management options to control mocó populations (VI) point to those more adequate options for the protected area (VII) ongoing work on rat eradication on offshore islets of Noronha. | |
| 9 | Juliana Gaeta (Universidade Federal do Ceará –UFC e Fundação Cearense de Apoio ao Desenvolvimento Científico e Tecnológico – FUNCAP); Raúl Cruz (UFC e FUNCAP) Rodrigo Maggioni (UFC); Annie Machordom (Museo Nacional Ciencias Naturales de Madrid, Spain) | (I)identify lobsters populations structure and the habitat use by them in Atol das Rocas; (II) update the list of lobsters from Rocas Atoll; (III) to provide information on distribution and density of all lobsters across the various habitats in the ecosystem of Rocas Atoll, meant to constitute an initial step toward identification of the population structure and habitat use of the several lobster species there present; (IV) assess the patterns of genetic connectivity among Panulirus echinatus oceanic island populations; (V) to evaluate sanitary status in Panulirus echinatus populations that could be infected with virus (WSSV, PaV1) and other pathogens which are known to cause disease and mortality in other spiny lobster species. |
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